DigitalDigital RepositoryERepository-ISSN 2549-8703 UniversitasIUniversitas P-ISSN 2302-7282 Jember Jember BIOTROPIKA Journal of Tropical Biology https://biotropika.ub.ac.id/ Vol. 9 | No. 1 | 2021 | DOI: 10.21776/ub.biotropika.2021.009.01.04 BUFFER ZONE MANAGEMENT IMPACT ON ASSEMBLAGE IN THE HIGH NATURE VALUE FARMLAND (HNVf): A STUDY CASE ON MERU BETIRI NATIONAL PARK

DAMPAK PENGELOLAAN ZONA PENYANGGA PADA SUSUNAN BURUNG- BURUNG DI HIGH NATURE VALUE FARMLAND (HNVf): SEBUAH STUDI KASUS PADA TAMAN NASIONAL MERU BETIRI

Nilasari Dewi1), Agung Sih Kurnianto1)*

Received : March 9th, 2021 ABSTRACT This study aims to analyze the distribution of communities and the impact of Accepted : April 10th, 2021 vegetation on bird habitat preferences in the buffer zone. Research is carried out in agricultural areas in the Buffer zone, Rehabilitation Zone, and on the edge of the plantation. The research location was determined at 37 points: Rajekwesi (4), Sukamade (12), Bandealit (8), Wonoasri (5), Andongrejo (3), Sanenrejo (5). We applied the point count method (r = 17.5 m) in this study, where each point is at Author Affiliation: least 100-150 meters apart. In the study, 74.6% of records were birds with agricultural specialities and 71.30% of individuals on tree habitats. Birds with 1) Agrotechnology Study Program, specialization in agriculture were found in large numbers related to the Agriculture Faculty, University of protection provided by the TNMB conservation area to bird habitat. Sukamade is Jember, Kalimantan street no. 37, the area with the highest number of records. As many as 40.10% were found in Jember, East Java Province, tree habitats followed by seedling (16.28%), poles (15.93%), flying over Indonesia (15.76%), and sapling (11.90%).

Keywords: birds, buffer zone, HNVf, MBNP

Alamat Korespondensi: ABSTRAK Penelitian ini bertujuan untuk menganalisis distribusi komunitas burung dan *[email protected] dampak vegetasi pada preferensi habitat di zona penyangga. Penelitian dilakukan di areal pertanian di Zona Penyangga, Zona Rehabilitasi, dan di pinggir perkebunan. Lokasi penelitian ditentukan di 37 titik yaitu Rajekwesi (4),

Sukamade (12), Bandealit (8), Wonoasri (5), Andongrejo (3), Sanenrejo (5). Kami

menerapkan metode hitung titik (r = 17,5 m) dalam penelitian ini, di mana setiap

titik setidaknya berjarak 100-150 meter. Dalam studi tersebut, 74,6% dari catatan How to cite: adalah burung dengan spesialisasi pertanian dan 71,30% individu yang Dewi, N, AS Kurnianto. 2021. menggunakan habitat pohon. Burung dengan spesialisasi di bidang pertanian Buffer zone management impact banyak ditemukan terkait dengan perlindungan yang diberikan kawasan on birds assemblage in the High konservasi TNMB terhadap habitat burung. Sukamade merupakan kawasan Nature Value Farmland (HNVf): dengan jumlah pencatatan terbanyak. Sebanyak 40,10% ditemukan di habitat a study case on Meru Betiri pohon, disusul seedling (16,28%), poles (15,93%), flying over (15,76%), dan sapling (11,90%). National Park. Journal of

Tropical Biology 9 (1): 27-37. Kata kunci: burung, HNVf, TNMB, zona penyangga

INTRODUCTION giving an agricultural effect to this conservation area. MBNP is also directly Buffer zones are unique in their potential adjacent to residential and agricultural pockets function of supporting protected areas. The that provide urban influences in a emergence of problems generally comes from rehabilitation zone. Low-intensity the economic and social needs of the managing characteristics of traditional farming systems community [1]. Meru Betiri National Park are associated with high biodiversity, (MBNP) is unique, where agricultural areas especially in conservation areas. support forest conservation and are managed HNV farmland is a land definition idea that traditionally to create sustainable management. began in the 1990s, where there was an There are two plantation companies in the increase in the conversion of forest national park that have quite a large area, thus Dewi & Kurnianto 27 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember degradation to agricultural areas and evaluating the quality of the diversity under settlements so that the role of conservation investigation. Based on these records, potential areas emerged in agricultural areas [2]. Low knowledge gaps in the HNVf study will be intensive and traditionally managed agriculture explored, which can be useful in future is one of the characteristics of the HNV knowledge challenges, which will contribute to agricultural area. The development of HNV the development of HNVf that maintains agricultural research concluded the definitions biodiversity. of the three types of HNV agriculture proposed in 2004: 1) Agricultural areas with a high METHODS proportion of semi-natural vegetation, 2) Study area. Research is carried out in Agricultural areas with mozaic from low- agricultural areas in the buffer zone, intensity agricultural areas and buffer elements rehabilitation zone, and on the edge of the and nature, such as field margins, hedgerows, plantation. The research location was stone walls, patches of timber or shrubland determined at 37 points: Rajekwesi (4), areas, streams, etc., 3) Agricultural areas that Sukamade (12), Bandealit (8), Wonoasri (5), support endangered species or world Andongrejo (3), Sanenrejo (5), see Figure 1 population or high regional [2]. Based on this We estimated the vegetation composition of definition, the MBNP Buffer Zone is an HNVf the observed area using a map grid (10x10m), area, and a study is needed to analyze the where the results represent the average distribution of bird communities and the percentage of land cover at the observation impact of vegetation on bird habitat points (see Table 1). preferences in the buffer zone. Bird Vegetation type were then categorized communities are an important indicator of based on: seedling h: 0-1.5 m, sapling h: ≥1.5 HNVf and illustrate the role of these areas to m, d: 10 cm, poles d: 10-20 cm, tree d: >20 cm support MBNP conservation areas. (h: height, d: diameter). Birds that did not To achieve this aim, systematic research is perch but fly among the vegetation were more carried out on agricultural areas. The results of pronounced as flyovers. the analysis focus on the distribution of trends and geographic distributions and focus on

Figure 1. Map of Meru Betiri National Park, study points, and observed resorts. Keys = light grey: areas outside the national park; dark grey: Unobserved resorts; black: plantation company area 28 Biotropika: Journal of Tropical Biology | Vol. 9 No. 1 | 2021 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember Table 1. Vegetation cover and land management at total observation points (%)

Rajekwesi Sanenrejo Andongrejo Wonosari Bandealit Sukamade Agroforestry 53,7 17,3 39 22,7 42,7 19,3 Hedgerows 16,8 25,7 61 46,6 11 26,3 Cover crops 29,5 0 0 30,3 46,2 37,7 Rainfed 0 56,8 0 0 0 16,3

protection, and 13 bird species had Birds survey. We applied the point count international trade protection (see Table 2). method (r = 17.5 m) in this study, where each Relative importance of HNV farmland point was at least 100-150 meters apart. The for bird. The importance values index (IVI) survey was conducted weekly for 15 minutes varies by species (see Table 2). The Cave between 06.00-09.00 am, which was the best Swiftlet was present to dominate and become active behaviour time for most birds. We an important species of all observed habitats recorded a bird that was observed or heard at (IVI = 10.95). Coppersmith Barbet followed each point. We avoided work during rainy, with a value of IVI = 8.45, and next was the cloudy, windy, or foggy days. Birds that had a Gray-cheeked Green-pigeon (IVI = 5.33). relationship with the observation location but A total of 284 records, or covering 54% of not perched were classified under flying over birds in Rajekwesi recorded used agroforest (FO). We used a Bushnell 10x70x70 binocular habitat. In Sanenrejo, as many as 88 to identify bird species, a Canon EOS 1100 D individuals, or 56% of the birds found used + 300 mm camera Canon Lens for taking rainfeds. A total of 142 individuals, or 61% of photos, and a Sony ICD-PX40 digital recorder the total birds found in Andongrejo had a to record bird sounds. Birds were identified by habitat in hedgerows. The same evidence was a bird identification field guide book [3]. We found in Wonoasri, where 43 individuals or confirmed bird sounds by comparing them to 46% of the total record, had habitat in the online xeno-canto bird sound database hedgerows. On Sukamade, cover crops were (http: //xeno-canto.org). the habitats most visited by birds, with 216 Data analysis. The bird identification data records, or 37% (see Figure 3). were then tabulated with Microsoft Excel In general, agroforestry systems with a 2007, then classified based on species, family, mixture of crops, such as coconut (Cocos conservation status, protection, and specialists nucifera) or sengon (Falcataria moluccana) in forest, forest edge, agriculture, or urban and other commodity crops underneath, were habitats [3]. preferred by birds, compared to other

monocultures rainfed or cover crops, like RESULTS AND DISCUSSION cassava, corn, and bean. All three had uniform During the point count at 37 points, we vegetation types and tend not to provide observed a total of 2135 birds comprising 156 suitable microhabitat, equal and low canopy species (Table S1, supplementary material). height. This made insectivores and carnivores Among them, there were 31 forest specialists concentrated on several edges that had a (439 individuals), 33 forest edge specialist combination of vegetation with a higher species (158 individuals), 73 specialist canopy. Canopy diversity had been shown to agricultural bird species (1095 individuals), have a positive effect on bird diversity. The and 13 urban area specialist birds (427 results showed that the canopy in the middle individuals). Three hundred and forty-five had the highest number of birds [4]. Next, the individuals flew over the observation point; mixed area, which was more than two types of 365 individuals were observed using the pole plants, provided a habitat role for a limited vegetation level, 152 individuals using the number of forest specialists, such as Olive- sapling level, 359 using the seedling vegetation winged Bulbul, Yellow-vented flowerpecker, level, and 898 using the tree vegetation level Wreathed hornbill, Javan-hawk Eagle, Rufous- (see Figure 2). There were three species that beliied Eagle, Sunda Coucal [3, 5]. had near threatened status, three species had Plant canopy in the constituent vulnerable status, and one species with agroecosystem gave preference to bird activity, endangered status. There were 30 species that including for protection. The intensity of are included in Indonesia's conservation utilization by birds was supported by the

Sari & Kurnianto 29 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember

100% 90% Sukamade 80% Bandealit 70% Wonosari 60% Andongrejo

bundance Sanen

a 50% Rajekwesi 40% 30% Relative 20% 10% 0%

A B

Figure 2. Comparison of relative abundance of birds in each area classified by vegetation type (A) and bird speciality (B) Agroforestry Hedgerows Cover crops Rainfed 300

250

200

150

100

50 number of of birdrecordnumber 0 Rajekwesi Sanen Andongrejo Wonosari Bandealit Sukamade Resort Area Figure 3. Number of birds finds in each resort area based on land type and vegetation availability of various foods sources in the conservation areas mainly because of its agroecosystem. The emergence of communal dependence on the natural forest as its roosting in the agroecosystem showed the breeding territory. However, now most of their activities carried out for several generations. lives were supported by open areas as prey Based on a comparison of the records in each providers, especially agricultural areas [5]. resort area, agriculture and urban specialist Green Peafowl was a protected species that birds had a unique capacity to adapt to most required open areas for foraging activities. research areas (Figure 2B). These bird species However, they required protection in woody had the ability to forage on forest edges and in vegetation at night [6]. urban areas, although there was less clear Urban birds were often present in interception with urban specialists. One of the residential areas and look for food leftovers species with the highest IVI value was from human activities [7] and had the ability to Coppersmith Barbet Megalaima haemacephala foraging in agricultural areas [8]. Other than (see table 2). This bird was a frugivore that had that, the Cave Swiftlet Collocalia linchi also a second large number and was adapted to had the ability to adapt in almost all research forest areas, edges, as well as in plantation and areas so that it had the highest IVI (see Table agricultural areas. In addition, agriculture 2). This species was an insectivore that grabs specialists got benefit from their food, which its prey in groups while flying. This was was available in abundance in open areas and supported by its anatomical system, which had forest edges, where this type of area was no cache [9]. Its large number in most areas covered very widely. Javan Hawk-Eagle was also affected the use of habitat by flyover (see one of the iconic, endemic, and rare species in Figure 2). TNMB. The limited distribution includes 30 Biotropika: Journal of Tropical Biology | Vol. 9 No. 1 | 2021 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember Table 2. The seven taxa with highest Important Value Index (IVI) and records of endangered and protected birds. Keys = Freq: Frequency, Abund. : Abundance, Div .: Shannon-Wiener Diversity Index, IVI: Important Value Index, Spec. : Bird Specialist, Ur: urban; Ag: Agroforest; F: Farmland; Fo: Forest; He: Hedgerows, IUCN: global conservation status (https://www.iucnredlist.org/), Protection: Permen LHK P.20 (A) and B CITES international trade agreement of endangered species (https://cites.org/ eng / app / index.php) Name/Species Freq. Abund. Div. IVI Spec. IUCN Protection Cave Swiftlet/Collocalia linchi 1.84 9.10 6.53 10.95 Ur Lc Coppersmith Barbet /Megalaima 1.84 6.60 3.54 8.45 Ag Lc haemacephala Grey-cheeked Green-pigeon / Treron 1.23 4.10 -1.09 5.33 Fo Lc griseicauda Yellow-vented Bulbul/Pycnonotus 1.53 3.68 -0.75 5.21 Fo Lc goiavier Sooty-headed Bulbul/Pycnonotus 1.84 3.35 -0.51 5.19 Ur Lc aurigaster Javan Munia/Lonchura leucogastroides 0.92 3.35 -0.51 4.27 Ag Lc Blue-eared barbet/Psilopogon australis 1.23 3.02 -0.51 4.25 Ag Lc A Threatened and protected bird Crested Goshawk/Accipiter trivirgatus 0.61 0.14 0.23 0.75 He Lc A.B Black Eagle/Ictinaetus malaiensis 0.31 0.04 0.10 0.35 F Lc A.B White-bellied Sea-eagle/Haliaeetus 0.61 0.09 0.17 0.70 He Lc A.B leucogaster Crested-serpent Eagle/Spilornis cheela 1.53 0.66 0.50 2.19 F Lc A.B Javan Hawk-eagle/Nisaetus bartelsi 0.61 0.09 0.17 0.70 F En A.B Rufous-bellied Eagle/Lopotriorchis 0.92 0.14 0.23 1.06 F Lc A.B kienerii Honey-buzzard/Pernis ptilorhynchus 0.92 0.18 0.27 1.11 F Lc A.B Oriental-pied Hornbill/Anthracoceros 0.61 1.69 0.39 2.31 Fo Lc A.B albirostris Wreathed Hornbill/Rhyticeros undulatus 0.92 2.12 0.22 3.04 Fo Lc A.B Rhinoceros Hornbill/Buceros rhinoceros 0.92 0.37 0.40 1.30 Fo Vu A.B Javan Coucal/Centropus nigrorufus 0.61 0.09 0.17 0.70 F Vu A Black-banded Barbet/Psilopogon javensis 0.92 2.64 -0.04 3.56 Fo Nt A Olive-backed Sunbird/Cinnyris jugularis 1.53 1.74 0.37 3.28 F Lc Dark-throated oriole/Oriolus xanthonotus 0.61 0.18 0.27 0.80 Fo Nt Green Peafowl/Pavo muticus 0.30 0.18 0.27 0.49 He Vu A.B Javan / strictus 0.61 0.09 0.17 0.70 Fo Vu Yellow-throated Hanging-parrot/Loriculus 0.92 1.03 0.52 1.96 He Nt A.B pusillus Sunda-pied Fantail/Rhipidura javanica 0.92 0.28 0.35 1.20 F Lc A

Coconut and sengon were combined cover Agricultural areas with traditional crops in the agroforestry system found in agroforest management were the most popular MBNP. These trees were common in all land habitat for birds. This was interesting, where cover types and became the most preferred the contribution of culture on traditional habitat for daily activities. However, figs trees agroforestry was large [10] and consisted of (Ficus sp.) gave more role in the cover crops various types of vegetation that can attract system than other types of trees. All various species of birds with many specialities. observation locations had figs, and it invited Agroforests were able to attract various types bird communities to engage in activities in the of to use them as a place of activity canopy and around it. The bird composition [8]. This was evident in various types of observed included insectivores, frugivores, and traditional agroforestry management in Java omnivores. Apart from activities in the canopy, and Sumatra, which were used as a variety of it was noted that the fig tree provided perches bird habitats, small mammals to large for beneficial bird communities, such as mammals such as elephants and Sumatran insectivores and nectarivorous for longer tigers [10]. However, agroforestry activities in the surrounding agricultural areas. management in TNMB is limited to semi- Sari & Kurnianto 31 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember traditional management by utilizing management most visited by birds. Most of the rehabilitated land [11]. The management did birds recorded were agricultural specialists and not use an adequate irrigation system and only use stratum levels of tree vegetation. The relies on various dryland commodities, like combination of coconut and sengon, as well as bananas and coffee. Other than that, jackfruit the crops below, attracts birds. In other, more (Artocarpus heterophyllus) and pete (Parkia open management type, figs are a major draw speciosa) were common plants at Resort for birds to visit. Wonoasri [12]. The high complexity of the role of birds ACKNOWLEDGEMENTS was seen in agroforest areas ranging from The authors thank the ranger and MBNP frugivores, insectivores, and observable for their assistance in the field and the carnivores. Frugivores were observed to make permission given. The first author would like greater use of some of the fig trees owned by to thank his partner on this research for the national park. It played an essential role in cooperation, guidance, and support. spreading tree seeds in areas with fragmented landscapes [13]. Its movement to REFERENCES heterogeneous landscapes also had an impact on the land cover [14]. Insectivores arise [1] Palomo I, Montes C, Martín-López B, because of the open area and cultivation of González JA, García-Llorente M, Alcorlo agricultural systems in them. 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Sari & Kurnianto 33 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember Table S1. Birds checklist on study Site. Keys = IUCN: global conservation status (https://www.iucnredlist.org/), Law: Permen LHK P.20,CITES: international trade agreement of endangered species (https://cites.org/eng/app/index.php) IUCN Resort Area No Nama Indonesia English Scientific Name Law Apppendix CITES NT Vu En Rajekwesi Sanen Andongrejo Wonosari Bandealit Sukamade 1 Remetuk Laut Golden-bellied gerygone Gerygone sulphurea 1 3 2 Elang Alap Jambul Crested goshawk Accipiter trivirgatus √ √ √ 2 1 3 Elang Hitam Black eagle Ictinaetus malaiensis √ √ √ 1 4 Elang Laut Perut Putih White-bellied sea eagle Haliaeetus leucogaster √ √ √ 1 1 5 Elang Ular Bido Crested serpent eagle Spilornis cheela √ √ √ 2 3 3 2 4 6 Elang Jawa Javan hawk-eagle Nisaetus bartelsi √ √ √ √ 1 1 7 Elang Brontok Changeable hawk-eagle Nisaetus cirrhatus √ 1 1 1 8 Elang Bondol Brahminy kite Haliastur indus √ 1 9 Elang-perut Karat Rufous-bellied eagle Lophotriorchis kienerii √ √ √ 1 1 1 10 Sikep-madu Asia Crested honey buzzard Pernis ptilorhynchus √ √ √ 1 1 2 11 Cipoh Kacat Common iora Aegithina tiphia 16 12 5 12 Cekakak Sungai Collared kingfisher Todiramphus chloris 6 2 2 12 13 Cekakak Jawa Javan kingfisher Halcyon cyanoventris 2 5 1 5 14 Cekakak Batu Banded kingfisher Lacedo pulchella 1 15 Cekakak Suci Sacred kingfisher Todiramphus sanctus 1 1 16 Udang Api Rufous-backed Kingfisher Ceyx rufidorsa 2 1 17 Raja-udang Meninting Blue-eared kingfisher Alcedo meninting 1 2 18 Walet Linci Cave swiftlet Collocalia linchi 42 34 45 15 34 23 19 Kapinis Rumah House swift Apus nipalensis 2 2 20 Walet Sapi Glossy swiftlet Collocalia esculenta 1 21 Kokokan Laut Striated heron Butorides striata 5 2 22 Cangak Merah Purple heron Ardea purpurea 2 2 23 Cangak Abu Grey heron Ardea cinerea 1 24 Blekok Sawah Javan pond heron Ardeola speciosa 2 25 Kuntul Karang Pacific reef heron Egretta sacra 2 2 26 Kuntul Kecil Little egret Egretta garzetta 1 27 Kuntul Kerbau Cattle egret Bubulcus ibis 2 28 Kowak Malam Abu Black-crowned night heron Nycticorax nycticorax 4 5 29 Kekep Babi White-breasted woodswallow Artamus leucorynchus 6 2 1 30 Kangkareng Perut Putih Oriental pied hornbill Anthracoceros albirostris √ √ √ 19 17 31 Julang Emas Wreathed hornbil Rhyticeros undulatus √ √ √ 16 16 13 32 Enggang Cula Rhinoceros hornbill Buceros rhinoceros √ √ √ 4 2 2 33 Sepah Kecil Small minivet Pericrocotus cinnamomeus 16 16 15 34 Sepah Hutan Orange minivet Pericrocotus flammeus 12 15 12 35 Sepah Gunung Sunda minivet Pericrocotus miniatus 2 36 Kapasan Sayap Putih White-shouldered triller Lalage sueurii 23 5 37 Kepudang-sungu Jawa Javan cuckooshrike Coracina javensis 2 2 38 Kepudang-sungu Kecil Lesser cuckooshrike Coracina fimbriata 1 1 39 Cabak Maling Large-tailed nightjar Caprimulgus macrurus 1 40 Cabak Kota Savanna nightjar Caprimulgus affinis 4 41 Cerek Jawa Javan plover Charadrius javanicus √ 2 2 42 Cica Daun Sayap Biru Blue-winged leafbird Chloropsis cochinchinensis √ 1 43 Bangau Sendang Lawe Woolly-necked stork Ciconia episcopus √ 3 2 1 4 2 44 Bangau Tongtong Lesser adjutant Leptoptilos javanicus √ 45 Cici Padi Zitting cisticola Cisticola juncidis 23 12 6 46 Perenjak Jawa Bar-winged prinia Prinia familiaris 13 23 2

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IUCN Resort Area No Nama Indonesia English Scientific Name Law Apppendix CITES NT Vu En Rajekwesi Sanen Andongrejo Wonosari Bandealit Sukamade 47 Cinenen Jawa Olive-backed tailorbird Orthotomus sepium 6 14 1 6 48 Cinenen Pisang Common tailorbird Orthotomus sutorius 6 2 49 Cinenen Kelabu Ashy tailorbird Orthotomus ruficeps 12 1 50 Delimukan Zamrud Common emerald dove Chalcophaps indica 1 1 51 Dederuk Jawa Sunda collared dove Streptopelia bitorquata 1 52 Tekukur Biasa Spotted dove Spilopelia chinensis 19 2 6 53 Walik Kembang Black-naped fruit dove Ptilinopus melanospilus 14 54 Perkutut Jawa Zebra dove Geopelia striata 1 55 Punai Penganten Grey-cheeked green pigeon Treron griseicauda 21 25 16 25 56 Punai Siam Orange-breasted green pigeon Treron bicinctus 1 57 Uncal Buau Ruddy cuckoo-dove Macropygia emiliana 2 58 Uncal Kouran Little cuckoo-dove Macropygia ruficeps 1 59 Pergam Hijau Green imperial pigeon Ducula aenea 3 60 Tiong-lampu Biasa Oriental dollarbird Eurystomus orientalis 2 2 61 Gagak Hutan Slender-billed crow Corvus enca 6 18 13 62 Tangkar Centrong Racket-tailed treepie Crypsirina temia 2 6 63 Bubut Alang-alang Lesser coucal Centropus bengalensis 2 6 5 64 Bubut Jawa Sunda coucal Centropus nigrorufus √ √ 1 1 65 Bubut Besar Greater coucal Centropus sinensis 1 66 Wiwik Lurik Banded bay cuckoo Cacomantis sonneratii 4 1 2 67 Wiwik Kelabu Plaintive cuckoo Cacomantis merulinus 2 2 68 Wiwik Uncuing Rusty-breasted cuckoo Cacomantis sepulcralis 1 69 Kedasi Ungu Violet cuckoo Chrysococcyx xanthorhynchus 1 70 Kangkok Ranting Himalayan cuckoo Cuculus saturatus 2 71 Kedasi Hitam Square-tailed drongo-cuckoo Surniculus lugubris 1 2 72 Kadalan Birah Chestnut-breasted malkoha Phaenicophaeus curvirostris 2 73 Kadalan Kembang Red-billed malkoha Phaenicophaeus javanicus 1 1 74 Cabai Jawa Scarlet-headed flowerpecker Dicaeum trochileum 5 2 75 Cabai Rimba Yellow-vented flowerpecker Dicaeum chrysorrheum 2 76 Cabai Bunga-api Orange-bellied flowerpecker Dicaeum trigonostigma 2 77 Srigunting Batu Greater racket-tailed drongo Dicrurus paradiseus 14 13 78 Srigunting Hitam Black drongo Dicrurus macrocercus 1 1 79 Bondol Jawa Javan munia Lonchura leucogastroides 34 21 16 80 Bondol Peking Scaly-breasted munia Lonchura punctulata 19 19 12 81 Bondol haji White-headed munia Lonchura maja 12 1 82 Sempur Hujan Rimba Banded broadbill Eurylaimus javanicus 2 1 83 Alap-alap Sapi Spotted kestrel Falco moluccensis √ 2 1 1 84 Alap-alap Capung Black-thighed falconet Microhierax fringillarius 2 2 85 Alap-alap Kawah Peregrine falcon Falco peregrinus √ 1 1 86 Tepekong Jambul Grey-rumped treeswift Hemiprocne longipennis 19 3 6 2 87 Layang-layang Batu Pacific swallow Hirundo tahitica 6 34 88 Layang-layang Loreng Striated swallow Cecropis striolata 7 1 89 Layang-layang Api Barn Swallow Hirundo rustica 14 4 12 9 90 Bentet Kelabu Long-tailed shrike Lanius schach 12 2 2 91 Cica-koreng Jawa Striated grassbird Megalurus palustris 17 1 92 Takur Tulung Tumpuk Black-banded barbet Megalaima javensis √ √ 23 19 14 93 Takur Bultok Lineated barbet Megalaima lineata 1 94 Takur Ungkut-ungkut Coppersmith barbet Megalaima haemacephala 54 19 23 16 12 16 95 Takur Tenggeret Blue-eared barbet Psilopogon cyanotis 18 12 21 13 96 Kirik-kirik Senja Chestnut-headed bee-eater Merops leschenaulti 21 6 6 10 Sari & Kurnianto 35 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember

IUCN Resort Area No Nama Indonesia English Scientific Name Law Apppendix CITES NT Vu En Rajekwesi Sanen Andongrejo Wonosari Bandealit Sukamade 97 Kehicap Ranting Black-naped monarch Hypothymis azurea 2 98 Kicuit Kerbau Western Yellow Wagtail Motacilla flava 2 99 Sikatan Cacing Hill blue flycatcher Cyornis banyumas 1 100 Meninting Besar White-crowned forktail Enicurus leschenaulti 1 1 101 Meninting Kecil Sunda forktail Enicurus velatus 1 102 Burung Madu Sriganti Olive-backed sunbird Cinnyris jugularis 5 6 12 12 2 103 Burung Madu Kelapa Brown-throated sunbird Anthreptes malacensis 4 1 2 104 Burungmadu Belukar Ruby-cheeked sunbird Chalcoparia singalensis 1 105 Burung-madu Sepah-Raja Crimson sunbird Aethopyga siparaja √ 1 106 Burung-madu Jawa Javan sunbird Aethopyga mystacalis √ 1 107 Pijantung Kecil Little spiderhunter Arachnothera longirostra 1 1 108 Pijantung Gunung Streaky-breasted spiderhunter Arachnothera affinis 2 1 109 Pijantung Besar Long-billed spiderhunter Arachnothera robusta 2 1 110 Kepudang Kuduk-hitam Black-naped oriole Oriolus chinensis 1 111 Kepudang Hutan Dark-throated oriole Oriolus xanthonotus √ 2 2 112 Kacembang Gadung Asian fairy-bluebird Irena puella 1 113 Burung Gereja Erasia Eurasian tree sparrow Passer montanus 2 114 Pelanduk Semak Horsfield's babbler Malacocincla sepiaria 5 1 2 115 Pelanduk Topi Hitam Black-capped babbler Pellorneum capistratum 2 1 116 Ayam Hutan Hijau Green junglefowl Gallus varius 12 8 8 117 Ayam Hutan Merah Red junglefowl Gallus gallus 1 118 Merak Hijau Green peafowl Pavo muticus √ √ √ √ 4 119 Pelatuk Ayam White-bellied Dryocopus javensis 2 120 Pelatuk Sayap merah Crimson-winged woodpecker Picus puniceus 2 2 121 Pelatuk Tunggir-emas Chrysocolaptes guttacristatus √ 1 1 122 Pelatuk Besi Common flameback Dinopium javanense 1 123 Pelatuk Kelabu Besar Great slaty woodpecker Mulleripicus pulverulentus 1 124 Caladi Tilik Sunda pygmy woodpecker Dendrocopos moluccensis 2 6 125 Caladi Ulam Fulvous-breasted woodpecker Dendrocopos macei 2 21 2 3 2 126 Caladi Tikotok grey-and-buff woodpecker Hemicircus sordidus 1 2 127 Paok Pancawarna Javan banded pitta Hydrornis guajana √ 3 5 3 128 Manyar Jambul Streaked weaver Ploceus manyar 21 129 Paruh-kodok Jawa Javan frogmouth Batrachostomus javensis 2 130 Serindit Jawa Yellow-throated hanging parrot Loriculus pusillus √ √ √ √ 14 6 2 131 Merbah Cerukcuk Yellow-vented bulbul Pycnonotus goiavier 16 4 42 3 13 132 Cuca Kutilang Sooty-headed bulbul Pycnonotus aurigaster 14 14 12 14 1 16 133 Cuca Kuricang Black-headed bulbul) Pycnonotus atriceps 2 2 134 Cuca Kuning Black-capped bulbul Pycnonotus melanicterus 16 4 2 135 Merbah Belukar Olive-winged bulbul Pycnonotus plumosus 9 1 13 136 Merbah Corok-corok Cream-vented bulbul Pycnonotus simplex 2 5 137 Empuloh Janggut Brown-cheeked bulbul Alophoixus bres 1 138 Kareo Padi White-breasted waterhen Amaurornis phoenicurus 1 1 139 Kipasan Belang Malaysian pied fantail Rhipidura javanica √ 2 2 2 140 Trinil Pantai Common sandpiper Actitis hypoleucos 2 141 Munguk Beledu Velvet-fronted nuthatch Sitta frontalis 12 6 4 142 Dara-laut Batu Bridled tern Onychoprion anaethetus √ 1 143 Dara-laut Kecil Little tern Sternula albifrons √ 1 144 Dara-laut Tiram Gull-billed tern Gelochelidon nilotica √ 1 145 Celepuk Reban Sunda scops owl Otus lempiji 2 146 Beluk Ketupa Buffy fish owl Ketupa ketupu √ √ 1 36 Biotropika: Journal of Tropical Biology | Vol. 9 No. 1 | 2021 DigitalDigital RepositoryRepositoryhttps://biotropika.ub.ac.id/ UniversitasUniversitas JemberJember

IUCN Resort Area No Nama Indonesia English Scientific Name Law Apppendix CITES NT Vu En Rajekwesi Sanen Andongrejo Wonosari Bandealit Sukamade 147 Kerak Kerbau Javan myna Acridotheres javanicus 6 12 6 148 Perling Kumbang Asian glossy starling Aplonis panayensis 12 2 149 Perling Kecil Short-tailed starling Aplonis minor 8 2 1 150 Jingjing Batu Black-winged flycatcher-shrike Hemipus hirundinaceus 9 2 12 151 Jingjing Petulak Large woodshrike Tephrodornis gularis 1 152 Tepus Pipi Perak Crescent-chested babbler Stachyris melanothorax 4 4 153 Ciung-air Jawa Grey-cheeked tit-babbler Macronus flavicollis 2 2 154 Luntur Harimau Orange-breasted trogon Harpactes oreskios 1 1 155 Gemak Loreng Barred buttonquail Turnix suscitator 1 1 156 Gemak Tegalan Common buttonquail Turnix sylvaticus 1

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